Overview
This source page is a mechanical bulk-ingest record for a PDF in the research-pulls corpus. It preserves source-level identity, routeable product/analyte scope, and exact extracted numeric lines for later human or fresh-context audit. It does not derive HMTc thresholds, percentiles, or brand-by-brand comparisons.
Key numbers
The worker extracted the full PDF text with layout preservation twice and compared extraction hashes before commit. The following lines are copied from numeric/table-bearing regions of the PDF and retain the source units and wording where legible:
- as shown in Table 1.
- contains more than 15% of the daily requirement of a has been linked to an increased risk of depression (6).
- content in erythrocytes was approx. 19% lower). The
- (23,26). (mean Al concentrations were 37.4 µg/L, range 10.5-92.8
- water quality by the World Health Organization (WHO) 23.8-181.1 µg/L) (32).
- aluminium should not exceed 1 mg/kg body weight, a part of total dietary Al exposure which has been
- approximately 5% of the total oral intake of aluminium interpretation (33). Notwithstanding, it is speculated
- concentrations ≥ 433.3 µg/L). The mean Al concentration for drinking-water quality indicates that NH3 and NH4+
- in the water was 134.1 µg/L. However, the authors levels present well below quantity that may affect human
- warrant subsequent investigations (30). Rondeau et al. 200 mg/kg body weight. Concentrations in ground and
- (2009) revealed that high daily consumption of Al through surface water range from less than 0.2 mg/l to 3 mg/l
- An apparent relationship between Al in drinking groundwater sources. However, the annual mean NH3/
- al. in 1989. Al concentration exceeding 110 µg/L implied exceed 0.5 mg/l. The river drinking water sources are
- concentrations were found to not exceed 10 µg/L (31). investigated regions and fluctuate seasonally. Variable
- intake of Sb is 6 µg/kg body weight while drinking water Sb RBA. Additionally, Sb RBA values were negatively
- 90% after storage at room temperature for half a year, Furthermore, researchers showed that Sb-exposed mice
- Canada which have increased by only 19% under the same and kidneys, indicating dysfunction of these organs. The
- As exposure routes remain food, drinking water, and appeared at As levels in drinking water beyond 50 ppb.
- occupational milieu; however, arsenic in groundwater or The authors concluded that a threshold of 10 ppb, set
- WHO guideline value by10 µg/l (27,58,59). As toxicity neuropathy (69,70).
- poisoning with distinctive nausea, vomiting, abdominal mg/l iAs concentrations in drinking water during 1- and
- concentrations (not exceeding 50 µg/l) is associated with the only one As species in the cerebral cortex deposited
- drinking water beyond 50 µg/l) (65). The WHO recommends a guideline value for Ba
- Mochizuki et al. (2019) explored the relationship in drinking water at a level of 1300 µg/l. However,
- contamination by low-dose As in Myanmar. Subjective and be generally less than 100 µg/l (27).
- were approximately 10 ppb (parts per billion)), whereas of barium salts. Cardiovascular, gastrointestinal,
- Ba dose (ranging from 140 to 1400 µg/kg/day) induced and is characterized by high reactivity. Naturally, Li
- ganglion neurons. Morphological analysis showed low (< 0.04 mg/l), while concentrations in drinking water
- significantly higher Ba levels in the inner ears of rats may range from 1 to 10 µg/l (0.001 – 0.01 mg/l). Sources
- Fenu et al. (2021) described a case of suicide by (81). There is a wide range of studies, strongly indicating
- and kidneys, but with no distinctive alterations in the 0.48 and 27.4 µg/l (81). Additionally, Schrauzer and
- concentration at level 13 mg/l (13000 µg/l) (75). suicide but also homicide, rape, and other crimes such as
- the field of neurological problems (76). concentrations exceeded 70 µg/l (88). Similar results were
- that 12 µg/l might be recognized as a health-based Be 27.4 µg/l) and dementia or bipolar disorder (92). Fajardo
- from 3 to 539 µg/l. Taking into consideration the median however, a health-based value at levels of 0.4 mg/l has
- Li concentration of 40 µg/l, the age-adjusted AD mortality been proposed. Additionally, back to permissibility
- rate was significantly elevated when Li levels were < 40 troubles, Mn concentrations higher than 0.1 mg/l might
- above 40 µg/l (93). sanitary ware that seem to be immediately noticed by
- Schimodera et al. (2018) explored Li concentrations water consumers, and hence suggested value of 0.4 mg/l
- Interestingly, unlike the aforementioned studies, value of 0.4 mg/l (106). Elevated Mn concentrations are
- adverse health effects associated with Li exposure of 133 µg/l, leading to a reduction of 1% in Performance
- ranged from 0.6 to 30.7 µg/l. Furthermore, no association 2%, and reduction of 5% was associated with BMC at the
Methods (brief)
- As exposure through drinking water at relatively low As - dimethylated acid (DMA) were found, while DMA was
- an increased incidence rate of ischemic and hemorrhagic during 1 month.. Notably, iAs and DMA occurred in all
- stroke in Denmark. The dependence was stronger for brain regions, while DMA appeared as the prevailing
-
- Fu Q, Zheng B, Zhao X, Wang L, Liu C. Ammonia pollution K, Lodh D, Biswas BK, Chanda CR, Basu GK, Saha KC, Roy S, Das
- ammonium-induced neurotoxicity. Neuroprotective effect 63. Ersbøll AK, Monrad M, Sørensen M, Baastrup R, Hansen B, Bach
- of alpha-2 adrenergic agonists. Arch Biochem Biophys. FW, Tjønneland A, Overvad K, Raaschou-Nielsen O. Low-level
-
- Filella M. Antimony and PET bottles: Checking facts. 67. Mukherjee SC, Rahman MM, Chowdhury UK, Sengupta MK, Lodh
- Aaseth J. Arsenic Toxicity: Molecular Targets and Therapeutic 75. Fenu EM, Brower JO, O’Neill TE. Suicide by an Unusual
- occurring lithium in drinking water and suicide rates: AC, Voskresenskaya ON, Aaseth J, Santamaria A, Notova SV,
-
- Teepker M, Hamer HM, Knake S, Bandmann O, Oertel WH, doi:10.4103/1673-5374.239434
- Toxicol. 2019 Apr;15(2):128-133. doi: 10.1007/s13181-018- in a community sample of South Korean school-age children.
- early childhood blood lead levels and performance on end-of- 171. Aastrup, M., Thunholm, B., Johnson, J., Bertills, U. and Berntell,
- Aaseth J, Chirumbolo S. Uranium in drinking water: a public
Implications
This page makes the source discoverable for category-level evidence routing. Values remain source-native and should be used only with the stated matrix, species, basis, geography, and censoring context from the paper. The page does not convert total mercury to methylmercury or use total arsenic as inorganic arsenic.
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Verification notes
- Identity check: DOI, raw handle, candidate cite-key, and SHA-256 were compared against existing
wiki/sources/pages before creation. - Full-PDF read:
pdftotext -layoutwas run on the full PDF twice; extracted text hashes matched before the page was written. - Numeric verification: numeric/table-bearing lines were selected mechanically from the verified extraction and preserved without unit conversion or rounding.
- Brand firewall: the worker skips PDFs when extracted numeric lines appear brand/manufacturer-sensitive; this page contains category-level or species-level evidence only.
- HMTc firewall: no threshold, percentile, pass/fail, clean/dirty, or certification math is stated.
Update history
The five most recent substantive edits to this page, classified major (evidence or structure moved), correction (a published value or statement was wrong and has been fixed), or minor (narrative rewritten without changing the underlying evidence). Each description is derived from what the edit did to this page; the linked commit is the authoritative record, routine regeneration passes are excluded, and the full version history lives in git. When DOI minting comes online (see schema docs), each entry below will also link to a version-pinned DataCite DOI.